Dicamba (Human Health Related, Incl

Total Page:16

File Type:pdf, Size:1020Kb

Dicamba (Human Health Related, Incl Dicamba (human health related, incl. rodent studies) 20110909 1. Kimura O, Tsukagoshi K, Hayasaka M, Endo T. 2011 Jul 16. Uptake of triclopyr (3,5,6-trichloro-2- pyridinyloxyacetic acid) and dicamba (3,6-dichloro-2-methoxybenzoic acid) from the apical membranes of the human intestinal Caco-2 cells. Arch Toxicol . Abstract: We investigated whether the uptake of triclopyr (3, 5, 6-trichloro-2-pyridinyloxyacetic acid) and dicamba (3,6-dichloro-2- methoxybenzoic acid) across the apical membrane of Caco-2 cells was mediated via proton-linked monocarboxylic acid transporters (MCTs). The uptake of triclopyr from the apical membranes was fast, pH-, temperature-, and concentration dependent, required metabolic energy to proceed, and was competitively inhibited by monocarboxylic acids such as benzoic acid and ferulic acid (substrates of L: -lactic acid-insensitive MCTs), but not by L: -lactic acid. Thus, the uptake of triclopyr in Caco-2 cells appears to be mediated mainly via L: -lactic acid-insensitive MCTs. In contrast, the uptake of dicamba (a benzoic acid derivative) was slow, and it was both pH- and temperature dependent. Coincubation with ferulic acid did not decrease the uptake of dicamba, although coincubation with benzoic acid moderately decreased it. The uptake of dicamba appears to be mediated mainly via passive diffusion, which is in contrast to the uptake of benzoic acid via MCTs. We speculate that the substituted groups in dicamba may inhibit uptake via MCTs. 2. Band PR, Abanto Z, Bert J, Lang B, Fang R, Gallagher RP, Le ND. 2011 Feb 1. Prostate cancer risk and exposure to pesticides in British Columbia farmers. Prostate 71(2 ):168-83. Abstract: BACKGROUND: Several epidemiologic studies have reported an increased risk of prostate cancer among farmers. Our aim was to assess the risk of developing prostate cancer in relation to exposure to specific active compounds in pesticides. METHOD: A case-control approach was used with 1,516 prostate cancer patients and 4,994 age-matched internal controls consisting of all other cancer sites excluding lung cancer and cancers of unknown primary site. Lifetime occupational history was obtained through a self-administered questionnaire and used in conjunction with a job exposure matrix to estimate the participants' lifetime cumulative exposure to approximately 180 active compounds in pesticides. Conditional logistic regression was used to assess prostate cancer risk, adjusting for potential confounding variables and effect modifiers. These include age, ethnicity, alcohol consumption, smoking, education, and proxy respondent. RESULTS AND CONCLUSIONS: The significant association between prostate cancer risk and exposure to DDT (OR = 1.68; 95% CI: 1.04-2.70 for high exposure), simazine (OR = 1.89; 95% CI: 1.08-3.33 for high exposure), and lindane (OR = 2.02; 95% CI: 1.15-3.55 for high exposure) is in keeping with those previously reported in the literature. We also observed a significant excess risk for several active ingredients that have not been previously reported in the literature such as dichlone, dinoseb amine, malathion, endosulfan, 2,4-D, 2,4-DB, and carbaryl. Some findings in our study were not consistent with those reported in the literature, including captan, dicamba, and diazinon. It is possible that these findings showed a real association and the inconsistencies reflected differences of characteristics between study populations. 3. Greco L, Pellerin J, Capri E, Garnerot F, Louis S, Fournier M , Sacchi A, Fusi M, Lapointe D, Couture P. 2011 Jan. Physiological effects of temperature and a herbicide mixture on the soft-shell clam Mya arenaria (Mollusca, Bivalvia). Environ Toxicol Chem 30(1):132-41. Abstract: The aim of the current study was to investigate effects of temperature and a mixture of herbicides on the physiological status of the bivalve Mya arenaria. Bivalves acclimated to two temperatures (7 and 18 degrees C) were exposed for 28 d to 0.01 mg/L of a pesticide formulation containing dichlorophenoxyacetic acid (2,4-D), 2-(2-methyl-4-chlorophenoxy) propionic acid (mecoprop), and 3,6-dichloro-2-methoxybenzoic acid (dicamba). At days 7, 14, and 28, mortality, immune parameters (hemocyte number, phagocytic activity, and efficiency), biomarkers of oxidative stress (catalase [CAT] and superoxide dismutase [SOD] activities and malondialdehyde [MDA] content), the metabolic enzyme cytochrome C oxidase (CCO), a biomarker of pesticide exposure (acetylcholinesterase [AChE]), and the activity of an enzyme related to gametogenesis (aspartate transcarbamylase [ATCase]) were monitored in clam tissues. Gonadosomatic index (GSI), condition factor (CF), and sex were also assessed. In clams acclimated to 7 degrees C, exposure to pesticide enhanced CCO activity and CF and decreased MDA content, hemocyte number, CAT, and SOD 1 activities. In clams kept at 18 degrees C, pesticide effects appeared minor compared with samples kept at 7 degrees C. In bivalves acclimated to 18 degrees C, CCO, SOD, and ATCase activity and MDA content were enhanced, and hemocyte number, CAT, and AchE activities and phagocytosis were suppressed. In samples exposed to pesticides, increased temperature enhanced MDA content and CCO and SOD activity and suppressed hemocyte number and CAT and AchE activity. A gradual sexual maturation was observed in both sexes through experimental time, but females had a higher sensitivity to temperature and pesticides compared to males. Increased temperature altered the ability of the sentinel species Mya arenaria to respond to pesticide exposures. Further work is needed to understand the impacts of increasing temperature on the whole St. Lawrence estuary ecosystem. 4. Brkic D, Gasic S, Radivojevic L, Szakonyne-Pasics I, Karan V, Neskovic N. 2011 . Avalon (R) (bentazon plus dicamba) herbicide: Subchronic toxicity to rats. Toxicol Lett 205 Suppl 1:S228-S229. 5. Harris SA, Villeneuve PJ, Crawley CD, Mays JE, Yeary RA, Hurto KA, Meeker JD. 2010 Sep 22. National study of exposure to pesticides among professional applicators: an investigation based on urinary biomarkers. J Agric Food Chem 58(18):10253-61. Abstract: Epidemiologic studies of pesticides have been subject to important biases arising from exposure misclassification. Although turf applicators are exposed to a variety of pesticides, these exposures have not been well characterized. This paper describes a repeated measures study of 135 TruGreen applicators over three spraying seasons via the collection of 1028 urine samples. These applicators were employed in six cities across the United States. Twenty-four-hour estimates (mug) were calculated for the parent compounds 2,4-D, MCPA, mecoprop, dicamba, and imidacloprid and for the insecticide metabolites MPA and 6-CNA. Descriptive statistics were used to characterize the urinary levels of these pesticides, whereas mixed models were applied to describe the variance apportionment with respect to city, season, individual, and day of sampling. The contributions to the overall variance explained by each of these factors varied considerably by the type of pesticide. The implications for characterizing exposures in these workers within the context of a cohort study are discussed. 6. Weichenthal S, Moase C, Chan P. 2010 Aug. A review of pesticide exposure and cancer incidence in the Agricultural Health Study cohort. Environ Health Perspect 118(8):1117-25. Abstract: OBJECTIVE: We reviewed epidemiologic evidence related to occupational pesticide exposures and cancer incidence in the Agricultural Health Study (AHS) cohort. DATA SOURCES: Studies were identified from the AHS publication list available at http://aghealth.nci.nih.gov as well as through a Medline/PubMed database search in March 2009. We also examined citation lists. Findings related to lifetime-days and/or intensity-weighted lifetime-days of pesticide use are the primary focus of this review, because these measures allow for the evaluation of potential exposure-response relationships. DATA SYNTHESIS: We reviewed 28 studies; most of the 32 pesticides examined were not strongly associated with cancer incidence in pesticide applicators. Increased rate ratios (or odds ratios) and positive exposure-response patterns were reported for 12 pesticides currently registered in Canada and/or the United States (alachlor, aldicarb, carbaryl, chlorpyrifos, diazinon, dicamba, S-ethyl-N,N-dipropylthiocarbamate, imazethapyr, metolachlor, pendimethalin, permethrin, trifluralin). However, estimates of association for specific cancers were often imprecise because of small numbers of exposed cases, and clear monotonic exposure-response patterns were not always apparent. Exposure misclassification is also a concern in the AHS and may limit the analysis of exposure-response patterns. Epidemiologic evidence outside the AHS remains limited with respect to most of the observed associations, but animal toxicity data support the biological plausibility of relationships observed for alachlor, carbaryl, metolachlor, pendimethalin, permethrin, and trifluralin. CONCLUSIONS: Continued follow-up is needed to clarify associations reported to date. In particular, further evaluation of registered pesticides is warranted. 7. Mukherjee M, Muraleedharannair P, Karmakar UK, Datta BK, Sar TK, Chakraborty AK, Bhattacharya A, Choudhury A, Mandal TK. 2010 Jan 30. Toxicokinetics and recovery studies of dicamba dimethyl amine salt in goats following single oral administration. J Sci Food Agric 90(2):257-66. Abstract: BACKGROUND: Toxicokinetics and recovery studies of dicamba
Recommended publications
  • Evolution of Resistance to Auxinic Herbicides: Historical Perspectives, Mechanisms of Resistance, and Implications for Broadleaf Weed Management in Agronomic Crops J
    Weed Science 2011 59:445–457 Evolution of Resistance to Auxinic Herbicides: Historical Perspectives, Mechanisms of Resistance, and Implications for Broadleaf Weed Management in Agronomic Crops J. Mithila, J. Christopher Hall, William G. Johnson, Kevin B. Kelley, and Dean E. Riechers* Auxinic herbicides are widely used for control of broadleaf weeds in cereal crops and turfgrass. These herbicides are structurally similar to the natural plant hormone auxin, and induce several of the same physiological and biochemical responses at low concentrations. After several decades of research to understand the auxin signal transduction pathway, the receptors for auxin binding and resultant biochemical and physiological responses have recently been discovered in plants. However, the precise mode of action for the auxinic herbicides is not completely understood despite their extensive use in agriculture for over six decades. Auxinic herbicide-resistant weed biotypes offer excellent model species for uncovering the mode of action as well as resistance to these compounds. Compared with other herbicide families, the incidence of resistance to auxinic herbicides is relatively low, with only 29 auxinic herbicide-resistant weed species discovered to date. The relatively low incidence of resistance to auxinic herbicides has been attributed to the presence of rare alleles imparting resistance in natural weed populations, the potential for fitness penalties due to mutations conferring resistance in weeds, and the complex mode of action of auxinic herbicides in sensitive dicot plants. This review discusses recent advances in the auxin signal transduction pathway and its relation to auxinic herbicide mode of action. Furthermore, comprehensive information about the genetics and inheritance of auxinic herbicide resistance and case studies examining mechanisms of resistance in auxinic herbicide-resistant broadleaf weed biotypes are provided.
    [Show full text]
  • 2,4-Dichlorophenoxyacetic Acid
    2,4-Dichlorophenoxyacetic acid 2,4-Dichlorophenoxyacetic acid IUPAC (2,4-dichlorophenoxy)acetic acid name 2,4-D Other hedonal names trinoxol Identifiers CAS [94-75-7] number SMILES OC(COC1=CC=C(Cl)C=C1Cl)=O ChemSpider 1441 ID Properties Molecular C H Cl O formula 8 6 2 3 Molar mass 221.04 g mol−1 Appearance white to yellow powder Melting point 140.5 °C (413.5 K) Boiling 160 °C (0.4 mm Hg) point Solubility in 900 mg/L (25 °C) water Related compounds Related 2,4,5-T, Dichlorprop compounds Except where noted otherwise, data are given for materials in their standard state (at 25 °C, 100 kPa) 2,4-Dichlorophenoxyacetic acid (2,4-D) is a common systemic herbicide used in the control of broadleaf weeds. It is the most widely used herbicide in the world, and the third most commonly used in North America.[1] 2,4-D is also an important synthetic auxin, often used in laboratories for plant research and as a supplement in plant cell culture media such as MS medium. History 2,4-D was developed during World War II by a British team at Rothamsted Experimental Station, under the leadership of Judah Hirsch Quastel, aiming to increase crop yields for a nation at war.[citation needed] When it was commercially released in 1946, it became the first successful selective herbicide and allowed for greatly enhanced weed control in wheat, maize (corn), rice, and similar cereal grass crop, because it only kills dicots, leaving behind monocots. Mechanism of herbicide action 2,4-D is a synthetic auxin, which is a class of plant growth regulators.
    [Show full text]
  • Aerobic and Anaerobic Bacterial and Fungal Degradation of Pyrene: Mechanism Pathway Including Biochemical Reaction and Catabolic Genes
    International Journal of Molecular Sciences Review Aerobic and Anaerobic Bacterial and Fungal Degradation of Pyrene: Mechanism Pathway Including Biochemical Reaction and Catabolic Genes Ali Mohamed Elyamine 1,2 , Jie Kan 1, Shanshan Meng 1, Peng Tao 1, Hui Wang 1 and Zhong Hu 1,* 1 Key Laboratory of Resources and Environmental Microbiology, Department of Biology, Shantou University, Shantou 515063, China; [email protected] (A.M.E.); [email protected] (J.K.); [email protected] (S.M.); [email protected] (P.T.); [email protected] (H.W.) 2 Department of Life Science, Faculty of Science and Technology, University of Comoros, Moroni 269, Comoros * Correspondence: [email protected] Abstract: Microbial biodegradation is one of the acceptable technologies to remediate and control the pollution by polycyclic aromatic hydrocarbon (PAH). Several bacteria, fungi, and cyanobacteria strains have been isolated and used for bioremediation purpose. This review paper is intended to provide key information on the various steps and actors involved in the bacterial and fungal aerobic and anaerobic degradation of pyrene, a high molecular weight PAH, including catabolic genes and enzymes, in order to expand our understanding on pyrene degradation. The aerobic degradation pathway by Mycobacterium vanbaalenii PRY-1 and Mycobactetrium sp. KMS and the anaerobic one, by the facultative bacteria anaerobe Pseudomonas sp. JP1 and Klebsiella sp. LZ6 are reviewed and presented, to describe the complete and integrated degradation mechanism pathway of pyrene. The different microbial strains with the ability to degrade pyrene are listed, and the degradation of Citation: Elyamine, A.M.; Kan, J.; pyrene by consortium is also discussed.
    [Show full text]
  • USDA, Forest Service Forest Health Protection GSA Contract No
    SERA TR 02-43-13-03b Triclopyr - Revised Human Health and Ecological Risk Assessments Final Report Prepared for: USDA, Forest Service Forest Health Protection GSA Contract No. GS-10F-0082F USDA Forest Service BPA: WO-01-3187-0150 USDA Purchase Order No.: 43-1387-2-0245 Task No. 13 Submitted to: Dave Thomas, COTR Forest Health Protection Staff USDA Forest Service Rosslyn Plaza Building C, Room 7129C 1601 North Kent Street Arlington, VA 22209 Submitted by: Patrick R. Durkin Syracuse Environmental Research Associates, Inc. 5100 Highbridge St., 42C Fayetteville, New York 13066-0950 Telephone: (315) 637-9560 Fax: (315) 637-0445 E-Mail: [email protected] Home Page: www.sera-inc.com March 15, 2003 TABLE OF CONTENTS LIST OF APPENDICES ...................................................... iv LIST OF WORKSHEETS ...................................................... v LIST OF ATTACHMENTS .................................................... v LIST OF TABLES ............................................................ v LIST OF FIGURES ......................................................... viii ACRONYMS, ABBREVIATIONS, AND SYMBOLS .............................. ix COMMON UNIT CONVERSIONS AND ABBREVIATIONS ......................... xi CONVERSION OF SCIENTIFIC NOTATION .................................... xii EXECUTIVE SUMMARY ................................................... xiii 1. INTRODUCTION ........................................................ 1-1 2. PROGRAM DESCRIPTION ................................................ 2-1 2.1. OVERVIEW
    [Show full text]
  • I. Signal Words and Warning Signs
    1 I. SIGNAL WORDS AND WARNING SIGNS Signal words are required on nearly all pesticide products registered and labeled for sale in the United States. The signal word gives a pesticide user a way to quickly assess the relative hazard level associated with using a product. There are three signal words in use today: CAUTION, WARNING and DANGER. note: The value “Oral LD50” (Low Dose 50) is a measurement of amount of pesticide (mg/kg) that kills 50 out of 100 laboratory animals that are force fed the pesticide under study. 2 These three signal words are associated with toxicity categories established by the U.S. Environmental Protection Agency (EPA). These four categories can be roughly described as: o Toxicity category I is Highly toxic and Severely irritating, o Toxicity category II is Moderately toxic and Moderately irritating, o Toxicity category III is Slightly toxic and Slightly irritating, o Toxicity category IV is practically non-toxic and not an irritant. LD50/LC50: A common measure of acute toxicity is the lethal dose (LD50) or lethal concentration (LC50) that causes death (resulting from a single or limited exposure) in 50 percent of the treated animals. LD50 is generally expressed as the dose in milligrams (mg) of chemical per kilogram (kg) of body weight. LC50 is often expressed as mg of chemical per volume (e.g., liter (L)) of medium (i.e., air or water) the organism is exposed to. Chemicals are considered highly toxic when the LD50/LC50 is small and practically non-toxic when the value is large. However, the LD50/LC50 does not reflect any effects from long-term exposure (i.e., cancer, birth defects or reproductive toxicity) that may occur at levels below those that cause death.
    [Show full text]
  • The Harmful Effects of Food Preservatives on Human Health Shazia Khanum Mirza1, U.K
    Journal of Medicinal Chemistry and Drug Discovery ISSN: 2347-9027 International peer reviewed Journal Special Issue Analytical Chemistry Teacher and Researchers Association National Convention/Seminar Issue 02, Vol. 02, pp. 610-616, 8 January 2017 Available online at www.jmcdd.org To Study The Harmful Effects Of Food Preservatives On Human Health Shazia Khanum Mirza1, U.K. Asema2 And Sayyad Sultan Kasim3. 1 -Research student , Dept of chemistry, Maulana Azad PG & Research centre, Aurangabad. 2-3 -Assist prof. Dept of chemistry,Maulana Azad college Arts sci & com.Aurangabad. ABSTRACT Food chemistry is the study of chemical processes and interactions of all biological and non- biological components. Food additives are chemicals added to foods to keep them fresh or to enhance their color, flavor or texture. They may include food colorings, flavor enhancers or a range of preservatives .The chemical added to a particular food for a particular reason during processing or storage which could affect the characteristics of the food, or become part of the food Preservatives are additives that inhibit the growth of bacteria, yeasts, and molds in foods. Additives and preservatives are used to maintain product consistency and quality, improve or maintain nutritional value, maintain palatability and wholesomeness, provide leavening(yeast), control pH, enhance flavour, or provide colour Some additives have been used for centuries; for example, preserving food by pickling (with vinegar), salting, as with bacon, preserving sweets or using sulfur dioxide as in some wines. Some preservatives are known to be harmful to the human body. Some are classified as carcinogens or cancer causing agents. Keywords : Food , Food additives, colour, flavour , texture, preservatives.
    [Show full text]
  • Herbicide Mode of Action Table High Resistance Risk
    Herbicide Mode of Action Table High resistance risk Chemical family Active constituent (first registered trade name) GROUP 1 Inhibition of acetyl co-enzyme A carboxylase (ACC’ase inhibitors) clodinafop (Topik®), cyhalofop (Agixa®*, Barnstorm®), diclofop (Cheetah® Gold* Decision®*, Hoegrass®), Aryloxyphenoxy- fenoxaprop (Cheetah®, Gold*, Wildcat®), fluazifop propionates (FOPs) (Fusilade®), haloxyfop (Verdict®), propaquizafop (Shogun®), quizalofop (Targa®) Cyclohexanediones (DIMs) butroxydim (Factor®*), clethodim (Select®), profoxydim (Aura®), sethoxydim (Cheetah® Gold*, Decision®*), tralkoxydim (Achieve®) Phenylpyrazoles (DENs) pinoxaden (Axial®) GROUP 2 Inhibition of acetolactate synthase (ALS inhibitors), acetohydroxyacid synthase (AHAS) Imidazolinones (IMIs) imazamox (Intervix®*, Raptor®), imazapic (Bobcat I-Maxx®*, Flame®, Midas®*, OnDuty®*), imazapyr (Arsenal Xpress®*, Intervix®*, Lightning®*, Midas®* OnDuty®*), imazethapyr (Lightning®*, Spinnaker®) Pyrimidinyl–thio- bispyribac (Nominee®), pyrithiobac (Staple®) benzoates Sulfonylureas (SUs) azimsulfuron (Gulliver®), bensulfuron (Londax®), chlorsulfuron (Glean®), ethoxysulfuron (Hero®), foramsulfuron (Tribute®), halosulfuron (Sempra®), iodosulfuron (Hussar®), mesosulfuron (Atlantis®), metsulfuron (Ally®, Harmony®* M, Stinger®*, Trounce®*, Ultimate Brushweed®* Herbicide), prosulfuron (Casper®*), rimsulfuron (Titus®), sulfometuron (Oust®, Eucmix Pre Plant®*, Trimac Plus®*), sulfosulfuron (Monza®), thifensulfuron (Harmony®* M), triasulfuron (Logran®, Logran® B-Power®*), tribenuron (Express®),
    [Show full text]
  • Exposure to Herbicides in House Dust and Risk of Childhood Acute Lymphoblastic Leukemia
    Journal of Exposure Science and Environmental Epidemiology (2013) 23, 363–370 & 2013 Nature America, Inc. All rights reserved 1559-0631/13 www.nature.com/jes ORIGINAL ARTICLE Exposure to herbicides in house dust and risk of childhood acute lymphoblastic leukemia Catherine Metayer1, Joanne S. Colt2, Patricia A. Buffler1, Helen D. Reed3, Steve Selvin1, Vonda Crouse4 and Mary H. Ward2 We examine the association between exposure to herbicides and childhood acute lymphoblastic leukemia (ALL). Dust samples were collected from homes of 269 ALL cases and 333 healthy controls (o8 years of age at diagnosis/reference date and residing in same home since diagnosis/reference date) in California, using a high-volume surface sampler or household vacuum bags. Amounts of agricultural or professional herbicides (alachlor, metolachlor, bromoxynil, bromoxynil octanoate, pebulate, butylate, prometryn, simazine, ethalfluralin, and pendimethalin) and residential herbicides (cyanazine, trifluralin, 2-methyl-4- chlorophenoxyacetic acid (MCPA), mecoprop, 2,4-dichlorophenoxyacetic acid (2,4-D), chlorthal, and dicamba) were measured. Odds ratios (OR) and 95% confidence intervals (CI) were estimated by logistic regression. Models included the herbicide of interest, age, sex, race/ethnicity, household income, year and season of dust sampling, neighborhood type, and residence type. The risk of childhood ALL was associated with dust levels of chlorthal; compared to homes with no detections, ORs for the first, second, and third tertiles were 1.49 (95% CI: 0.82–2.72), 1.49 (95% CI: 0.83–2.67), and 1.57 (95% CI: 0.90–2.73), respectively (P-value for linear trend ¼ 0.05). The magnitude of this association appeared to be higher in the presence of alachlor.
    [Show full text]
  • 40 CFR Ch. I (7–1–18 Edition) § 455.61
    § 455.61 40 CFR Ch. I (7–1–18 Edition) from: the operation of employee show- § 455.64 Effluent limitations guidelines ers and laundry facilities; the testing representing the degree of effluent of fire protection equipment; the test- reduction attainable by the applica- ing and emergency operation of safety tion of the best available tech- showers and eye washes; or storm nology economically achievable water. (BAT). (d) The provisions of this subpart do Except as provided in 40 CFR 125.30 not apply to wastewater discharges through 125.32, any existing point from the repackaging of microorga- source subject to this subpart must nisms or Group 1 Mixtures, as defined achieve effluent limitations rep- under § 455.10, or non-agricultural pes- resenting the degree of effluent reduc- ticide products. tion attainable by the application of the best available technology economi- § 455.61 Special definitions. cally achievable: There shall be no dis- Process wastewater, for this subpart, charge of process wastewater pollut- means all wastewater except for sani- ants. tary water and those wastewaters ex- § 455.65 New source performance cluded from the applicability of the standards (NSPS). rule in § 455.60. Any new source subject to this sub- § 455.62 Effluent limitations guidelines part which discharges process waste- representing the degree of effluent water pollutants must meet the fol- reduction attainable by the applica- lowing standards: There shall be no dis- tion of the best practicable pollut- charge of process wastewater pollut- ant control technology (BPT). ants. Except as provided in 40 CFR 125.30 through 125.32, any existing point § 455.66 Pretreatment standards for existing sources (PSES).
    [Show full text]
  • Triclopyr Human Health and Ecological Risk Assessment Corrected Final Report
    SERA TR-052-25-03c Triclopyr Human Health and Ecological Risk Assessment Corrected Final Report Submitted to: Paul Mistretta, COR USDA/Forest Service, Southern Region 1720 Peachtree RD, NW Atlanta, Georgia 30309 USDA Forest Service Contract: AG-3187-C-06-0010 USDA Forest Order Number: AG-43ZP-D-09-0034 SERA Internal Task No. 52-25 Submitted by: Patrick R. Durkin Syracuse Environmental Research Associates, Inc. 8125 Solomon Seal Manlius, New York 13104 Fax: (315) 637-0445 E-Mail: [email protected] Home Page: www.sera-inc.com May 24, 2011 October 20, 2011 (Minor Correction) July 9, 2016 (Corrections) Error Notes October 20, 2011 In the original release of the final report (SERA TR-052-25-03a dated May 24, 2011), Tables 2 and 22 incorrectly listed the water solubility of TCP as 100 mg/L. As indicated in Table 1, the correct value, from Knuteson (1999), is 49,000 mg/L. This error was noted by Dr. K. King (U.S. Fish and Wildlife Service). The error has been corrected. While the Gleams-Driver runs were made using the 100 mg/L water solubility, re-runs using the water solubility of 49,000 mg/L yielded results that are indistinguishable from the original runs. Thus, the appendices have not been change. Water solubility is not a sensitive parameter in GLEAMS unless the soil water is saturated. This did not occur in the Gleams-Driver modeling. July 9, 2016 During an audit of WorksheetMaker (Version 6.00.15), it was noted that the chronic toxicity values of TCP to aquatic invertebrates had been entered incorrectly into the WorksheetMaker database and the aquatic toxicity values of TCP for algae had been omitted.
    [Show full text]
  • INDEX to PESTICIDE TYPES and FAMILIES and PART 180 TOLERANCE INFORMATION of PESTICIDE CHEMICALS in FOOD and FEED COMMODITIES
    US Environmental Protection Agency Office of Pesticide Programs INDEX to PESTICIDE TYPES and FAMILIES and PART 180 TOLERANCE INFORMATION of PESTICIDE CHEMICALS in FOOD and FEED COMMODITIES Note: Pesticide tolerance information is updated in the Code of Federal Regulations on a weekly basis. EPA plans to update these indexes biannually. These indexes are current as of the date indicated in the pdf file. For the latest information on pesticide tolerances, please check the electronic Code of Federal Regulations (eCFR) at http://www.access.gpo.gov/nara/cfr/waisidx_07/40cfrv23_07.html 1 40 CFR Type Family Common name CAS Number PC code 180.163 Acaricide bridged diphenyl Dicofol (1,1-Bis(chlorophenyl)-2,2,2-trichloroethanol) 115-32-2 10501 180.198 Acaricide phosphonate Trichlorfon 52-68-6 57901 180.259 Acaricide sulfite ester Propargite 2312-35-8 97601 180.446 Acaricide tetrazine Clofentezine 74115-24-5 125501 180.448 Acaricide thiazolidine Hexythiazox 78587-05-0 128849 180.517 Acaricide phenylpyrazole Fipronil 120068-37-3 129121 180.566 Acaricide pyrazole Fenpyroximate 134098-61-6 129131 180.572 Acaricide carbazate Bifenazate 149877-41-8 586 180.593 Acaricide unclassified Etoxazole 153233-91-1 107091 180.599 Acaricide unclassified Acequinocyl 57960-19-7 6329 180.341 Acaricide, fungicide dinitrophenol Dinocap (2, 4-Dinitro-6-octylphenyl crotonate and 2,6-dinitro-4- 39300-45-3 36001 octylphenyl crotonate} 180.111 Acaricide, insecticide organophosphorus Malathion 121-75-5 57701 180.182 Acaricide, insecticide cyclodiene Endosulfan 115-29-7 79401
    [Show full text]
  • The Effect Off Ethylenediamine Tetraacetic Acid 4 the Antimicrobial Properties of Benzoic
    University of Nigeria Virtual Library Serial No ISSN: 1118-1028 Author 1 MBAH, Chika J. Author 2 Author 3 Title The Effect of Ethylenediamine Tetraacetic Acid on the Antimicrobial Properties of Benzoic Acid and Cetrimide Keywords Description Pharmaceutical Chemistry Category Pharmaceutical Sciences Publisher Publication Date 1999 Signature * - ' 8 - . 1 I r/ Journal of I PHARMACEUTICAL 1 RESEARCH AND i .DEVELOPMENT Journal of Pharmaceutical Research and Development 4: 1 (1 999) 1 -8 - 1 : The Effect offEthylenediamine Tetraacetic Acid 4 the Antimicrobial Properties of Benzoic ) Acid and Cetrimide C. 0. Esirnonel* M. U. ~dikwu';D.B. Uzuegbu' and 0. P. Udeo 4 'Division of Pharmaceutical Microbiology Department of Pharmz Faculty of Phyackutical Sciences University of Nigeria, Ws I 'Department of ~harmacolo~~and Toxicology, Faculty of Pharmaceut ' . University of Nigeria,fisukka. i I I : I. The effect of ethylenediamine tetraacetic acid (EDTA) on the in-vp antimicrobial activities of cetrimide and benzoic acid was evaluated by the checkerboardland killing curve method. The effect sf EDTA aid benzoic acid was evaluated against an isolate of Pseirdonionas aeruginosa (Ps. 021) which is highly resistant to either of the drugs alone. The effect of EDTA and cetrimide was evaluated against isolates of Aspergillus niger and Candidn albicarls resistant to either of the agents. The results show that in the'presence of EDTA, the bacteriostatic and bactericidal effects of benzoic acid and cetrimide against the test microorgan,isms were greatly enhanced. Checkerboard analy& revealed striking synergy (FIC indices > 1 and negative values of activity indices) between almost all the ratios of EDTA and the antimicrobial agents against the various test microorganisms.
    [Show full text]